Deprecated: The each() function is deprecated. This message will be suppressed on further calls in /home/zhenxiangba/zhenxiangba.com/public_html/phproxy-improved-master/index.php on line 456
JP3347481B2 - Exhaust gas purification catalyst - Google Patents
[go: Go Back, main page]

JP3347481B2 - Exhaust gas purification catalyst - Google Patents

Exhaust gas purification catalyst

Info

Publication number
JP3347481B2
JP3347481B2 JP16408894A JP16408894A JP3347481B2 JP 3347481 B2 JP3347481 B2 JP 3347481B2 JP 16408894 A JP16408894 A JP 16408894A JP 16408894 A JP16408894 A JP 16408894A JP 3347481 B2 JP3347481 B2 JP 3347481B2
Authority
JP
Japan
Prior art keywords
exhaust gas
catalyst
palladium
platinum
supporting part
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Fee Related
Application number
JP16408894A
Other languages
Japanese (ja)
Other versions
JPH0824644A (en
Inventor
洋 平山
麻祐子 永井
容規 佐藤
慎次 松浦
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Cataler Corp
Toyota Motor Corp
Original Assignee
Cataler Corp
Toyota Motor Corp
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Cataler Corp, Toyota Motor Corp filed Critical Cataler Corp
Priority to JP16408894A priority Critical patent/JP3347481B2/en
Publication of JPH0824644A publication Critical patent/JPH0824644A/en
Application granted granted Critical
Publication of JP3347481B2 publication Critical patent/JP3347481B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters

Landscapes

  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
  • Catalysts (AREA)

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【産業上の利用分野】本発明は、自動車エンジンなどの
内燃機関からの排気ガス中に含まれる一酸化炭素(C
O)、炭化水素(HC)及び窒素酸化物(NOx)を同
時に除去する排気ガス浄化用触媒に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to carbon monoxide (C) contained in exhaust gas from an internal combustion engine such as an automobile engine.
O), a hydrocarbon (HC) and a nitrogen oxide (NOx).

【0002】[0002]

【従来の技術】従来より、自動車の排気ガス浄化用触媒
として、CO及びHCの酸化とNOxの還元とを同時に
行って排気ガスを浄化する三元触媒が用いられている。
このような三元触媒としては、例えばコーディエライト
などからなる耐熱性担体にγ−アルミナからなる触媒担
持層を形成し、その触媒担持層に白金、ロジウムなどの
白金族元素を担持させたものが広く知られている。ま
た、酸素貯蔵効果をもつセリア(酸化セリウム)を併用
し、低温活性を高めた三元触媒も知られている。
2. Description of the Related Art Conventionally, a three-way catalyst for purifying exhaust gas by simultaneously oxidizing CO and HC and reducing NOx has been used as an exhaust gas purifying catalyst for automobiles.
As such a three-way catalyst, for example, a catalyst-supporting layer made of γ-alumina is formed on a heat-resistant carrier made of cordierite or the like, and the catalyst-supporting layer supports a platinum group element such as platinum or rhodium. Is widely known. Also known is a three-way catalyst in which ceria (cerium oxide) having an oxygen storage effect is used in combination to enhance low-temperature activity.

【0003】ところで近年、排気ガス浄化用触媒の設置
場所がエンジンに近いマニホールド直下とされる傾向が
あり、また高速走行時には排気ガス温度が高くなること
から、排気ガス浄化用触媒は高温に晒される場合が多く
なっている。ところが白金族元素や酸化セリウムを担持
した排気ガス浄化用触媒は、高温において劣化しやすく
耐久後の浄化性能が低下するという不具合がある。その
ため希土類金属やアルカリ土類金属の酸化物をさらに担
持させたり、白金族元素として耐熱性の良好なパラジウ
ムを用いたりすることで、高温耐熱性を向上させること
が考えられている。
[0003] In recent years, the exhaust gas purifying catalyst is installed at a position immediately below a manifold close to the engine, and the exhaust gas temperature becomes high during high-speed running, so that the exhaust gas purifying catalyst is exposed to high temperatures. In many cases. However, an exhaust gas purifying catalyst supporting a platinum group element or cerium oxide tends to deteriorate at a high temperature and has a problem that purification performance after durability is reduced. Therefore, it has been considered to improve the high-temperature heat resistance by further supporting a rare earth metal or alkaline earth metal oxide or by using palladium having good heat resistance as a platinum group element.

【0004】ところがパラジウムは、リッチ雰囲気及び
理論空燃比(ストイキ)よりややリーン雰囲気側におけ
るNOxの浄化性能に劣っている。そのためパラジウム
のみではNOxの浄化は困難と考えられ、高いNOx浄
化性能を有するロジウムと併用することで三元触媒とし
て用いられている。しかしロジウムは非常に高価である
ので、高価な排気ガス浄化用触媒となってしまう。
However, palladium is inferior in NOx purification performance in a rich atmosphere and slightly leaner than the stoichiometric air-fuel ratio (stoichiometric). Therefore, it is considered that purification of NOx is difficult only with palladium, and it is used as a three-way catalyst when used in combination with rhodium having high NOx purification performance. However, since rhodium is very expensive, it becomes an expensive exhaust gas purifying catalyst.

【0005】そこで、白金族元素としてはパラジウムの
みを用い、他に酸化セリウム、バリウム化合物、ジルコ
ニウム化合物、ランタン酸化物、活性アルミナなどを含
む担持層をもち、安価で三元活性に優れた排気ガス浄化
用触媒が提案されている(特開平5-168926号公報、特開
平5-168927号公報)。
[0005] Therefore, only palladium is used as the platinum group element, and in addition to the above, the exhaust gas which has a carrier layer containing cerium oxide, barium compound, zirconium compound, lanthanum oxide, activated alumina, etc., is inexpensive and has excellent ternary activity. Purification catalysts have been proposed (Japanese Patent Laid-Open Nos. 5-168926 and 5-68927).

【0006】[0006]

【発明が解決しようとする課題】上記公報に開示されて
いるパラジウムに各種助触媒を組み合わせた三元触媒に
おいては、リッチ雰囲気側での水性ガスシフト反応(C
O+H2 O→CO2 +H 2 )や水蒸気改質反応(HC+
2 O→CO2 +H2 )を促進してNOxの浄化性能を
高めているが、特にストイキよりややリーン雰囲気側で
のNOx浄化性能は充分でない。
DISCLOSURE OF THE INVENTION Problems to be Solved by the Invention
Three-way catalyst combining palladium with various co-catalysts
The water gas shift reaction (C
O + HTwoO → COTwo+ H Two) And steam reforming reaction (HC +
HTwoO → COTwo+ HTwo) To improve NOx purification performance
Although it is raised, especially on the slightly lean side than stoichiometric
NOx purification performance is not sufficient.

【0007】本発明はこのような事情に鑑みてなされた
ものであり、触媒成分としてパラジウムを用いた三元触
媒を改良し、ストイキよりややリーン雰囲気側における
NOx浄化性能をさらに向上させることを目的とする。
The present invention has been made in view of the above circumstances, and an object of the present invention is to improve a three-way catalyst using palladium as a catalyst component to further improve NOx purification performance in a slightly leaner atmosphere than stoichiometric conditions. And

【0008】[0008]

【課題を解決するための手段】上記課題を解決する本発
明の排気ガス浄化用触媒は、三元触媒システムのフィー
ドバック制御が行われるエンジンから排出される排気ガ
スを浄化する排気ガス浄化用触媒であって、担体基材
と、担体基材表面に被覆形成された触媒担持層と、触媒
担持層に担持されたパラジウム、白金及びアルカリ土類
金属からなる触媒活性成分とから構成され、白金を排気
ガス流の流れ方向に対して上流側のみに担持したことを
特徴とする。
The exhaust gas purifying catalyst of the present invention which solves the above-mentioned problems is provided by a three-way catalyst system.
Exhaust gas discharged from the engine for which the feedback control is performed
An exhaust gas purifying catalyst for purifying exhaust gas, comprising a carrier substrate, a catalyst supporting layer formed on the surface of the carrier substrate, and a catalyst comprising palladium, platinum and an alkaline earth metal supported on the catalyst supporting layer. And platinum is supported only on the upstream side with respect to the flow direction of the exhaust gas flow.

【0009】[0009]

【作用】本発明の排気ガス浄化用触媒では、パラジウム
と白金及びアルカリ土類金属が担持されている。この触
媒では、リッチ雰囲気からリーン雰囲気のそれぞれの状
態の混合気から排出された排気ガス中のNOxは,以下
のようにして浄化される。 (1)リッチ雰囲気側 助触媒成分であるアルカリ土類金属が水性ガスシフト反
応や水蒸気改質反応を促進し、高いNOx浄化性能が得
られる。 (2)理論空燃比近傍 三元活性に優れるパラジウムが主としてNOxを浄化す
る。 (3)リーン雰囲気側 白金が主としてNOxを浄化する。
In the exhaust gas purifying catalyst of the present invention, palladium, platinum and an alkaline earth metal are supported. With this catalyst, NOx in the exhaust gas discharged from the air-fuel mixture in each state from the rich atmosphere to the lean atmosphere is purified as follows. (1) Rich atmosphere side The alkaline earth metal as a promoter component promotes a water gas shift reaction and a steam reforming reaction, and high NOx purification performance is obtained. (2) Near stoichiometric air-fuel ratio Palladium excellent in ternary activity mainly purifies NOx. (3) Lean atmosphere side Platinum mainly purifies NOx.

【0010】ところで、白金は空燃比(A/F)の振幅
が大きい条件下で浄化性能に優れるという特性をもって
いる。そこで本発明では、排気ガス流の上流側に白金を
担持している。これによりパラジウムとアルカリ土類金
属とを担持した従来の触媒に比べて、理論空燃比近傍及
びややリーン側のNOx浄化性能が向上する。なお、白
金担持部の占める体積が大きくなると、白金の特性が強
く現れるとともにパラジウムの三元活性に優れる特性が
低下し、理論空燃比近傍及びややリーン側のNOxの浄
化性能が低下する。したがって白金は担体全体積に対し
て15〜50%、好ましくは15〜30%の範囲で上流
側に担持するのが望ましい。
By the way, platinum has a characteristic that the purification performance is excellent under the condition that the amplitude of the air-fuel ratio (A / F) is large. Therefore, in the present invention, platinum is carried on the upstream side of the exhaust gas flow. This improves the NOx purification performance near the stoichiometric air-fuel ratio and slightly on the lean side as compared with the conventional catalyst supporting palladium and alkaline earth metal. When the volume occupied by the platinum-carrying portion increases, the characteristics of platinum appear strongly and the characteristics of palladium excellent in ternary activity decrease, and the purification performance of NOx near the stoichiometric air-fuel ratio and slightly on the lean side decreases. Therefore, it is desirable that platinum is supported on the upstream side in the range of 15 to 50%, preferably 15 to 30% based on the whole volume of the carrier.

【0011】また白金とパラジウムの担持量は、パラジ
ウムが白金より多く含まれているように構成すれば、理
論空燃比近傍における三元活性に優れるパラジウムの特
性と、リーン雰囲気側におけるNOx浄化性能に優れる
白金の特性のバランスが最適となり、理論空燃比近傍及
びややリーン雰囲気側のNOx浄化性能が向上する。特
に1/50≦Pt/Pd≦1/2の範囲が望ましい。
If the amount of supported platinum and palladium is configured so that palladium is contained in a larger amount than platinum, the characteristics of palladium excellent in ternary activity near the stoichiometric air-fuel ratio and the NOx purification performance in the lean atmosphere side are improved. The excellent balance of the characteristics of platinum is optimized, and the NOx purification performance near the stoichiometric air-fuel ratio and in a slightly leaner atmosphere is improved. In particular, the range of 1/50 ≦ Pt / Pd ≦ 1/2 is desirable.

【0012】[0012]

【実施例】以下、実施例により具体的に説明する。な
お、以下の例において「部」は特にことわらない限り
「重量部」を示す。 (実施例1)活性アルミナ粉末100部、酸化ジルコニ
ウムで安定化された酸化セリウム粉末40部、炭酸ラン
タン粉末30部、40wt% 硝酸アルミニウム水溶液65部
及び水80部を混合し、コーティング用スラリーを調製
した。
The present invention will be specifically described below with reference to examples. In the following examples, “parts” means “parts by weight” unless otherwise specified. Example 1 100 parts of activated alumina powder, 40 parts of cerium oxide powder stabilized with zirconium oxide, 30 parts of lanthanum carbonate powder, 65 parts of a 40 wt% aluminum nitrate aqueous solution and 80 parts of water were mixed to prepare a slurry for coating. did.

【0013】コーディエライト製のハニカム状モノリス
担体基材(体積1.3L、全長143.5mm)を水に
浸漬し、余分な水を吹き払った後、上記スラリーに浸漬
し、取り出した後余分なスラリーを吹き払い、250℃
で1時間乾燥後、500℃で1時間焼成して、アルミナ
を主とする触媒担持層を形成した。この触媒担持層のコ
ーティング量は、担体基材1L当たり190gである。
[0013] A cordierite honeycomb monolithic carrier substrate (volume 1.3 L, total length 143.5 mm) is immersed in water, excess water is blown off, then immersed in the slurry, taken out, and extracted. 250 ° C
For 1 hour, and calcined at 500 ° C. for 1 hour to form a catalyst supporting layer mainly composed of alumina. The coating amount of the catalyst supporting layer is 190 g per liter of the carrier substrate.

【0014】このようにして得た担体全体を、所定濃度
の硝酸パラジウム水溶液に1時間浸漬し、引き上げて余
分な水分を吹き払った後、250℃で乾燥した。次にパ
ラジウムを担持した担体全体を水に浸漬し、余分な水を
吹き払った後、所定濃度のジニトロジアンミン白金水溶
液中に上流側端面より65mmの部分のみ浸漬し、1時
間浸漬後引き上げて余分な水滴を吹き払った後、250
℃で乾燥した。
The entire carrier thus obtained was immersed in an aqueous solution of palladium nitrate having a predetermined concentration for 1 hour, pulled up to blow off excess water, and dried at 250 ° C. Next, the entire palladium-supported carrier is immersed in water, and excess water is blown off. Then, only the portion 65 mm from the upstream end surface is immersed in a predetermined concentration of dinitrodiammine platinum aqueous solution, and then immersed for 1 hour and pulled up for extra. 250
Dried at ° C.

【0015】さらに、パラジウム及び白金を担持した担
体全体を所定濃度の酢酸バリウム水溶液に1時間浸漬
し、引き上げて余分な水滴を吹き払った後、250℃で
乾燥した。得られた触媒1個当たりには、図1に示すよ
うにPdが3.3g(担持部密度:2.5g/L)、P
tが0.7g(担持部密度:1g/L)、Baが40g
(担持部密度:30g/L)担持されている。また、上
流側のPt担持部の長さは72mmで全体積の50%で
あり、PdとBaは担体全体に均一に担持されている。 (実施例2)実施例1と同様の触媒担持層をもつ担体全
体を水に浸漬し、余分な水を吹き払った後、所定濃度の
硝酸パラジウム水溶液に下流側端面より65mmの部分
を1時間浸漬し、引き上げて余分な水分を吹き払った
後、250℃で乾燥した。次にパラジウムを担持した担
体全体を水に浸漬し、余分な水を吹き払った後、所定濃
度のジニトロジアンミン白金水溶液中に上流側端面より
65mmの部分を浸漬し、1時間浸漬後引き上げて余分
な水滴を吹き払った後、250℃で乾燥した。
Further, the entire carrier supporting palladium and platinum was immersed in an aqueous barium acetate solution of a predetermined concentration for 1 hour, pulled up to blow off excess water droplets, and dried at 250 ° C. As shown in FIG. 1, 3.3 g of Pd (supporting portion density: 2.5 g / L) per one obtained catalyst,
t is 0.7 g (supporting part density: 1 g / L), Ba is 40 g
(Loading density: 30 g / L) Further, the length of the Pt carrying portion on the upstream side is 72 mm, which is 50% of the total volume, and Pd and Ba are carried uniformly on the whole carrier. (Example 2) The entire carrier having the same catalyst-supporting layer as in Example 1 was immersed in water, and excess water was blown off. Then, a portion 65 mm from the end face on the downstream side in an aqueous solution of palladium nitrate having a predetermined concentration was applied for 1 hour. It was immersed and pulled up to blow off excess water, and then dried at 250 ° C. Next, the entire palladium-supported carrier is immersed in water, and excess water is blown off. Then, a portion 65 mm from the upstream end face is immersed in an aqueous solution of dinitrodiammine platinum having a predetermined concentration. After blowing off water droplets, drying was performed at 250 ° C.

【0016】さらに、パラジウム及び白金を担持した担
体全体を所定濃度の酢酸バリウム水溶液に1時間浸漬
し、引き上げて余分な水滴を吹き払った後、250℃で
乾燥した。得られた触媒1個当たりには、図2に示すよ
うにPdが3.3g(担持部密度:5g/L)、Ptが
0.7g(担持部密度:1g/L)、Baが40g(担
持部密度:30g/L)担持されている。また、上流側
のPt担持部の長さは72mmで全体積の50%であ
り、下流側のPd担持部の長さも72mmで全体の50
%である。Baは担体全体に均一に担持されている。 (比較例1)実施例1と同様にして調製された触媒を上
流側と下流側を逆にして比較例1の触媒とした。つまり
各金属の担持量は、図5に示すようにPdが3.3g
(担持部密度:2.5g/L)、Ptが0.7g(担持
部密度:1g/L)、Baが40g(担持部密度:30
g/L)で実施例1と同様であるが、Pt担持部は下流
側に72mmで全体の50%形成され、PtとBaは担
体全体に均一に担持されている。 (比較例2)実施例2と同様にして調製された触媒を上
流側と下流側を逆にして比較例2の触媒とした。つまり
各金属の担持量は、図6に示すようにPdが3.3g
(担持部密度:5g/L)、Ptが0.7g(担持部密
度:1g/L)、Baが40g(担持部密度:30g/
L)で実施例2と同様であるが、Pt担持部は下流側に
72mmで全体の50%形成され、Pd担持部は上流側
に72mmで全体の50%形成されている。Baは担体
全体に均一に担持されている。 (比較例3)実施例1と同様の触媒担持層をもつ担体全
体を所定濃度の硝酸パラジウム水溶液に1時間浸漬し、
引き上げて余分な水分を吹き払った後、250℃で乾燥
した。次にパラジウムを担持した担体全体を所定濃度の
酢酸バリウム水溶液に1時間浸漬し、引き上げて余分な
水滴を吹き払った後、250℃で乾燥した。
Further, the entire carrier supporting palladium and platinum was immersed in an aqueous barium acetate solution of a predetermined concentration for 1 hour, pulled up to blow off excess water droplets, and dried at 250 ° C. As shown in FIG. 2, 3.3 g of Pd (supporting portion density: 5 g / L), 0.7 g of Pt (supporting portion density: 1 g / L), and 40 g of Ba per obtained catalyst (see FIG. 2). (Supporting part density: 30 g / L) Further, the length of the Pt carrying portion on the upstream side is 72 mm and 50% of the total volume, and the length of the Pd carrying portion on the downstream side is also 72 mm and 50% of the whole volume.
%. Ba is uniformly supported on the entire carrier. (Comparative Example 1) A catalyst prepared in the same manner as in Example 1 was used in Comparative Example 1 except that the upstream side and the downstream side were reversed. That is, as shown in FIG. 5, the amount of each metal carried was 3.3 g of Pd.
(Supporting part density: 2.5 g / L), Pt 0.7 g (supporting part density: 1 g / L), Ba 40 g (supporting part density: 30)
g / L) as in Example 1, except that the Pt supporting portion is formed 72 mm downstream and is 50% of the whole, and Pt and Ba are uniformly supported on the entire carrier. (Comparative Example 2) The catalyst prepared in the same manner as in Example 2 was used, except that the upstream side and the downstream side were reversed. That is, as shown in FIG. 6, the amount of each metal carried is 3.3 g of Pd.
(Supporting part density: 5 g / L), Pt: 0.7 g (supporting part density: 1 g / L), Ba: 40 g (supporting part density: 30 g / L)
L) is the same as that of the second embodiment, except that the Pt carrying portion is 72 mm on the downstream side and 50% of the whole is formed, and the Pd carrying portion is 72 mm on the upstream side and 50% of the whole. Ba is uniformly supported on the entire carrier. (Comparative Example 3) The entire carrier having the same catalyst-supporting layer as in Example 1 was immersed in an aqueous solution of palladium nitrate having a predetermined concentration for 1 hour.
After pulling up and blowing off excess water, drying was performed at 250 ° C. Next, the entire carrier supporting palladium was immersed in a barium acetate aqueous solution of a predetermined concentration for 1 hour, pulled up to blow off excess water droplets, and then dried at 250 ° C.

【0017】得られた触媒1個当たりには、図7に示す
ようにPdが3.9g(担持部密度:3g/L)、Ba
が40g(担持部密度:30g/L)担持されている。
PdとBaは担体全体に均一に担持されている。 (比較例4)実施例1と同様の触媒担持層をもつ担体全
体を所定濃度の硝酸パラジウム水溶液に1時間浸漬し、
引き上げて余分な水分を吹き払った後、250℃で乾燥
した。次にパラジウムを担持した担体全体を所定濃度の
ジニトロジアンミン白金水溶液中に1時間浸漬し引き上
げて余分な水滴を吹き払った後、250℃で乾燥した。
さらに、パラジウム及び白金を担持した担体全体を所定
濃度の酢酸バリウム水溶液に1時間浸漬し、引き上げて
余分な水滴を吹き払った後、250℃で乾燥した。
As shown in FIG. 7, 3.9 g of Pd (supporting part density: 3 g / L) and Ba
Is supported by 40 g (supporting portion density: 30 g / L).
Pd and Ba are uniformly supported on the entire carrier. (Comparative Example 4) The entire carrier having the same catalyst-supporting layer as in Example 1 was immersed in an aqueous solution of palladium nitrate having a predetermined concentration for 1 hour.
After pulling up and blowing off excess water, drying was performed at 250 ° C. Next, the entire carrier supporting palladium was immersed in an aqueous solution of dinitrodiammineplatinum of a predetermined concentration for 1 hour, pulled up to blow off excess water droplets, and then dried at 250 ° C.
Further, the entire carrier supporting palladium and platinum was immersed in a barium acetate aqueous solution of a predetermined concentration for 1 hour, pulled up to blow off excess water droplets, and then dried at 250 ° C.

【0018】得られた触媒1個当たりには、図8に示す
ようにPdが3.3g(担持部密度:2.5g/L)、
Ptが0.65g(担持部密度:0.5g/L)、Ba
が40g(担持部密度:30g/L)担持され、Pd,
Pt及びBaは担体全体に均一に担持されている。 (浄化性能の評価)上記のそれぞれの排気ガス浄化用触
媒を排気量2Lのエンジンの排気系に取り付け、排気ガ
ス温度800℃、A/F=14.6(ストイキ)の条件
で100時間運転する耐久試験を行った。
As shown in FIG. 8, 3.3 g of Pd (supporting part density: 2.5 g / L) per one obtained catalyst,
Pt is 0.65 g (supporting part density: 0.5 g / L), Ba
Is supported by 40 g (supporting portion density: 30 g / L), and Pd,
Pt and Ba are uniformly supported on the entire carrier. (Evaluation of Purification Performance) Each of the above exhaust gas purifying catalysts was attached to an exhaust system of an engine having a displacement of 2 L, and was operated for 100 hours at an exhaust gas temperature of 800 ° C. and an A / F of 14.6 (stoichiometric). A durability test was performed.

【0019】そして耐久試験後の各排気ガス浄化用触媒
の浄化性能をエンジンベンチで評価し、結果を表1に示
す。評価方法としては、排気ガス温度を400℃に維持
し、中心A/F=14.6(ストイキ)及び中心A/F
=14.8(ストイキよりややリーン)でのHC,C
O,NOxのそれぞれの浄化率を測定した。
The purification performance of each exhaust gas purifying catalyst after the durability test was evaluated on an engine bench, and the results are shown in Table 1. As an evaluation method, the exhaust gas temperature was maintained at 400 ° C., and the center A / F = 14.6 (stoichiometric) and the center A / F
HC, C at = 14.8 (slightly leaner than stoichiometric)
The purification rates of O and NOx were measured.

【0020】[0020]

【表1】 表1より、A/F=14.6(ストイキ)の条件下で
は、実施例及び比較例ともに良好な浄化性能を示しその
差は小さい。しかしストイキよりややリーンのA/F=
14.8の条件下では、NOx浄化性能に顕著な差が現
れ、Ptを上流側に担持した実施例の触媒が優れている
ことが明らかである。 (実施例3)図3に示すように、触媒1個当たりにして
Pdが3.3g(担持部密度:2.5g/L)、Ptが
0.40g(担持部密度:1g/L)、Baが40g
(担持部密度:30g/L)担持され、上流側のPt担
持部が全体積の30%であること以外は実施例1と同様
の構成である。 (実施例4)図4に示すように、触媒1個当たりにして
Pdが3.3g(担持部密度:2.5g/L)、Ptが
0.20g(担持部密度:1g/L)、Baが40g
(担持部密度:30g/L)担持され、上流側のPt担
持部が全体積の15%であること以外は実施例1と同様
の構成である。 (実施例5)触媒1個当たりにしてPdが3.3g(担
持部密度:2.5g/L)、Ptが0.14g(担持部
密度:1g/L)、Baが40g(担持部密度:30g
/L)担持され、上流側のPt担持部が全体積の10%
であること以外は実施例1と同様の構成である。 (実施例6)触媒1個当たりにしてPdが3.3g(担
持部密度:3.6g/L)、Ptが0.40g(担持部
密度:1g/L)、Baが40g(担持部密度:30g
/L)担持され、上流側のPt担持部が全体積の30
%、下流側のPd担持部が全体積の70%であること以
外は実施例2と同様の構成である。 (実施例7)触媒1個当たりにしてPdが3.3g(担
持部密度:3.0g/L)、Ptが0.20g(担持部
密度:1g/L)、Baが40g(担持部密度:30g
/L)担持され、上流側のPt担持部が全体積の15
%、下流側のPd担持部が全体積の85%であること以
外は実施例2と同様の構成である。 (実施例8)触媒1個当たりにしてPdが3.3g(担
持部密度:2.8g/L)、Ptが0.14g(担持部
密度:1g/L)、Baが40g(担持部密度:30g
/L)担持され、上流側のPt担持部が全体積の10
%、下流側のPd担持部が全体積の90%であること以
外は実施例2と同様の構成である。 (浄化性能の評価)上記の各実施例の排気ガス浄化用触
媒を排気量2Lのエンジンの排気系に取り付け、排気ガ
ス温度800℃、A/F=14.6(ストイキ)の条件
で100時間運転する耐久試験を行った。
[Table 1] From Table 1, under the condition of A / F = 14.6 (stoichiometric), both of the examples and the comparative examples show good purification performance and the difference is small. However, A / F = leaner than stoichiometric
Under the condition of 14.8, a remarkable difference appears in the NOx purification performance, and it is clear that the catalyst of the example in which Pt is carried on the upstream side is excellent. (Example 3) As shown in FIG. 3, Pd was 3.3 g (supporting part density: 2.5 g / L), Pt was 0.40 g (supporting part density: 1 g / L) per catalyst, Ba is 40g
(Supporting part density: 30 g / L) The structure is the same as that of Example 1 except that the Pt carrying part on the upstream side is 30% of the total volume. Example 4 As shown in FIG. 4, Pd was 3.3 g (supporting part density: 2.5 g / L), Pt was 0.20 g (supporting part density: 1 g / L) per catalyst. Ba is 40g
(Supporting part density: 30 g / L) The structure is the same as that of Example 1 except that the Pt carrying part on the upstream side is 15% of the total volume. (Example 5) 3.3 g of Pd (supporting part density: 2.5 g / L), 0.14 g of Pt (supporting part density: 1 g / L), and 40 g of Ba (supporting part density) per catalyst : 30g
/ L) carried, and the Pt carrying portion on the upstream side is 10% of the total volume
The configuration is similar to that of the first embodiment except that (Example 6) 3.3 g of Pd (supporting part density: 3.6 g / L), 0.40 g of Pt (supporting part density: 1 g / L), and 40 g of Ba (supporting part density) per catalyst : 30g
/ L) carried, and the upstream Pt carrying part has a total volume of 30%.
%, And the configuration is the same as that of the second embodiment except that the downstream Pd carrying portion is 70% of the total volume. (Example 7) Pd was 3.3 g (supporting part density: 3.0 g / L), Pt was 0.20 g (supporting part density: 1 g / L), and Ba was 40 g (supporting part density) per catalyst. : 30g
/ L) carried, and the upstream Pt carrying portion has a total volume of 15
%, And the configuration is the same as that of the second embodiment, except that the Pd carrying portion on the downstream side is 85% of the total volume. (Example 8) Per catalyst, 3.3 g of Pd (supporting part density: 2.8 g / L), 0.14 g of Pt (supporting part density: 1 g / L), and 40 g of Ba (supporting part density) : 30g
/ L) carried, and the upstream Pt carrying portion has a total volume of 10
%, And the configuration is the same as that of the second embodiment except that the downstream Pd carrying portion is 90% of the total volume. (Evaluation of Purification Performance) The exhaust gas purifying catalyst of each of the above embodiments was attached to an exhaust system of a 2 L engine, and the exhaust gas temperature was 800 ° C., and the A / F was 14.6 (stoichiometric) for 100 hours. A running durability test was performed.

【0021】そして耐久試験後の各排気ガス浄化用触媒
の浄化性能をエンジンベンチで評価し、結果を表2に示
す。評価方法としては、排気ガス温度を400℃に維持
し、中心A/F=14.6(ストイキ)及び中心A/F
=14.8(ストイキよりややリーン)でのHC,C
O,NOxのそれぞれの浄化率を測定した。
Then, the purifying performance of each exhaust gas purifying catalyst after the durability test was evaluated on an engine bench, and the results are shown in Table 2. As an evaluation method, the exhaust gas temperature was maintained at 400 ° C., and the center A / F = 14.6 (stoichiometric) and the center A / F
HC, C at = 14.8 (slightly leaner than stoichiometric)
The purification rates of O and NOx were measured.

【0022】[0022]

【表2】 実施例1,3,4,5の結果からわかるように、Pt担
持部が大きいほどストイキよりややリーン側(A/F=
14.8)におけるNOx浄化率が高くなり、Pt担持
部が30%以上でNOx浄化率が飽和している。したが
って、Ptの使用によるコスト上昇の面を考慮すると、
Pt担持部は15〜30%が最適である。なお、実施例
2,6,7,8の結果からも、Pt担持部は15〜30
%が最適であることがわかる。
[Table 2] As can be seen from the results of Examples 1, 3, 4, and 5, the larger the Pt carrying portion, the slightly leaner the stoichiometric side (A / F =
In 14.8), the NOx purification rate increased, and the NOx purification rate was saturated when the Pt carrying portion was 30% or more. Therefore, considering the cost increase due to the use of Pt,
The optimal amount of the Pt carrier is 15 to 30%. In addition, also from the results of Examples 2, 6, 7, and 8, the Pt carrying portion is 15 to 30.
It turns out that% is optimal.

【0023】なお、本発明に用いられる担体基材として
は、一体形構造のモノリス担体あるいはペレット担体な
どが用いられる。その材質としては、コーディエライ
ト、ムライト、α−アルミナ、アルミノ珪酸塩などのセ
ラミック質、あるいはFe−Cr−Al合金などの耐火
性金属質が例示される。触媒担持層としては、活性アル
ミナが望ましいが、場合によってはアルミナ、シリカ、
チタニアなどを用いることもできる。
As the carrier substrate used in the present invention, a monolithic carrier or a pellet carrier having an integral structure is used. Examples of the material include ceramics such as cordierite, mullite, α-alumina, and aluminosilicate, and refractory metals such as an Fe—Cr—Al alloy. As the catalyst support layer, activated alumina is desirable, but in some cases, alumina, silica,
Titania or the like can also be used.

【0024】さらにアルカリ土類金属としては、バリウ
ムが特に望ましいが、カルシウム、ストロンチウムを用
いることもできる。なお、これらと同時に酸化セリウ
ム、酸化ジルコニウム、酸化ランタンを含むことも好ま
しく、特に酸化セリウムを含むことが望ましい。
As the alkaline earth metal, barium is particularly desirable, but calcium and strontium can also be used. It is preferable that cerium oxide, zirconium oxide, and lanthanum oxide be contained at the same time, and it is particularly desirable that cerium oxide be contained.

【0025】[0025]

【発明の効果】すなわち本発明の排気ガス浄化用触媒に
よれば、ストイキよりややリーン側(A/F=14.
8)におけるNOxの浄化性能が向上する。またアルカ
リ土類金属により、リッチ側におけるNOxの浄化性能
が高まり、その結果A/Fに対するウインドウ幅の広い
触媒となっている。
That is, according to the exhaust gas purifying catalyst of the present invention, it is slightly leaner than the stoichiometric air (A / F = 14.
The purification performance of NOx in 8) is improved. Further, the alkaline earth metal enhances the NOx purification performance on the rich side, and as a result, the catalyst has a wide window width for A / F.

【0026】したがって一般の三元触媒システムのフィ
ードバック制御において、HC,CO,NOxの3成分
とも高い浄化性能を発揮することができる。
Therefore, in the feedback control of a general three-way catalyst system, all three components of HC, CO and NOx can exhibit high purification performance.

【図面の簡単な説明】[Brief description of the drawings]

【図1】本発明の実施例1の排気ガス浄化用触媒の構成
説明図である。
FIG. 1 is a configuration explanatory view of an exhaust gas purifying catalyst according to a first embodiment of the present invention.

【図2】本発明の実施例2の排気ガス浄化用触媒の構成
説明図である。
FIG. 2 is a configuration explanatory view of an exhaust gas purifying catalyst according to a second embodiment of the present invention.

【図3】本発明の実施例3の排気ガス浄化用触媒の構成
説明図である。
FIG. 3 is an explanatory diagram illustrating a configuration of an exhaust gas purifying catalyst according to a third embodiment of the present invention.

【図4】本発明の実施例4の排気ガス浄化用触媒の構成
説明図である。
FIG. 4 is a configuration explanatory view of an exhaust gas purifying catalyst according to a fourth embodiment of the present invention.

【図5】本発明の比較例1の排気ガス浄化用触媒の構成
説明図である。
FIG. 5 is an explanatory diagram of a configuration of an exhaust gas purifying catalyst of Comparative Example 1 of the present invention.

【図6】本発明の比較例2の排気ガス浄化用触媒の構成
説明図である。
FIG. 6 is an explanatory diagram of a configuration of an exhaust gas purifying catalyst of Comparative Example 2 of the present invention.

【図7】本発明の比較例3の排気ガス浄化用触媒の構成
説明図である。
FIG. 7 is an explanatory diagram of a configuration of an exhaust gas purifying catalyst of Comparative Example 3 of the present invention.

【図8】本発明の比較例4の排気ガス浄化用触媒の構成
説明図である。
FIG. 8 is an explanatory diagram of a configuration of an exhaust gas purifying catalyst of Comparative Example 4 of the present invention.

───────────────────────────────────────────────────── フロントページの続き (72)発明者 佐藤 容規 静岡県小笠郡大東町千浜7800番地 キャ タラー工業株式会社内 (72)発明者 松浦 慎次 静岡県小笠郡大東町千浜7800番地 キャ タラー工業株式会社内 (56)参考文献 特開 平5−317652(JP,A) 特開 昭61−78438(JP,A) 特開 昭61−234932(JP,A) (58)調査した分野(Int.Cl.7,DB名) B01J 21/00 - 38/74 B01D 53/86 B01D 53/94 F01N 3/00 - 3/02 F01N 3/04 - 3/38 F01N 9/00 ──────────────────────────────────────────────────続 き Continued on the front page (72) Inventor Yuki Sato 7800 Chihama, Daito-cho, Ogasa-gun, Shizuoka Prefecture Inside (72) Inventor Shinji Matsuura 7800 Chiba, Daito-cho, Ogasa-gun, Shizuoka Cataler (56) References JP-A-5-317652 (JP, A) JP-A-61-78438 (JP, A) JP-A-61-234932 (JP, A) (58) Fields studied (Int .Cl. 7 , DB name) B01J 21/00-38/74 B01D 53/86 B01D 53/94 F01N 3/00-3/02 F01N 3/04-3/38 F01N 9/00

Claims (1)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 三元触媒システムのフィードバック制御
が行われるエンジンから排出される排気ガスを浄化する
排気ガス浄化用触媒であって、 担体基材と、該担体基材表面に被覆形成された触媒担持
層と、該触媒担持層に担持されたパラジウム、白金及び
アルカリ土類金属からなる触媒活性成分とから構成さ
れ、白金を排気ガス流の流れ方向に対して上流側のみに
担持したことを特徴とする排気ガス浄化用触媒。
1. Feedback control of a three-way catalyst system
Purifies exhaust gases emitted from the engine
An exhaust gas purifying catalyst, comprising: a carrier substrate; a catalyst supporting layer formed on the surface of the carrier substrate; and a catalytically active component comprising palladium, platinum, and an alkaline earth metal supported on the catalyst supporting layer. And platinum only on the upstream side with respect to the flow direction of the exhaust gas flow.
An exhaust gas purifying catalyst which is carried .
JP16408894A 1994-07-15 1994-07-15 Exhaust gas purification catalyst Expired - Fee Related JP3347481B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP16408894A JP3347481B2 (en) 1994-07-15 1994-07-15 Exhaust gas purification catalyst

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP16408894A JP3347481B2 (en) 1994-07-15 1994-07-15 Exhaust gas purification catalyst

Publications (2)

Publication Number Publication Date
JPH0824644A JPH0824644A (en) 1996-01-30
JP3347481B2 true JP3347481B2 (en) 2002-11-20

Family

ID=15786552

Family Applications (1)

Application Number Title Priority Date Filing Date
JP16408894A Expired - Fee Related JP3347481B2 (en) 1994-07-15 1994-07-15 Exhaust gas purification catalyst

Country Status (1)

Country Link
JP (1) JP3347481B2 (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5753192A (en) * 1996-11-29 1998-05-19 Ford Global Technologies, Inc. Zirconia and sulfate in NOx traps to improved trapping and sulfur tolerance
JP5232401B2 (en) * 2007-04-05 2013-07-10 株式会社キャタラー Exhaust gas purification catalyst
US8758695B2 (en) * 2009-08-05 2014-06-24 Basf Se Treatment system for gasoline engine exhaust gas

Also Published As

Publication number Publication date
JPH0824644A (en) 1996-01-30

Similar Documents

Publication Publication Date Title
KR100196245B1 (en) Catalyst for purifying exhaust gases
US4500650A (en) Three-way catalysts for purification of exhaust gas and method for the preparation of the catalysts
JPH03207445A (en) Multi-functional catalyst for conversion of contaminant containing ce and u as well as metal exhausted from internal combustion engine, and preparation of said catalyst
JP3216858B2 (en) Exhaust gas purification catalyst and method for producing the same
JP3882627B2 (en) Exhaust gas purification catalyst
JP3798727B2 (en) Exhaust gas purification catalyst
JP3685463B2 (en) Exhaust gas purification catalyst
JPH08332350A (en) Exhaust gas purification catalyst
JP3789231B2 (en) Exhaust gas purification catalyst
JP2002045702A (en) Catalyst for purifying exhaust gas
JP3335755B2 (en) Exhaust gas purification catalyst
JPH07108172A (en) Exhaust gas purification catalyst and method for producing the same
JP3532979B2 (en) Exhaust gas purification catalyst
JP3224054B2 (en) Exhaust gas purification method
JP3347481B2 (en) Exhaust gas purification catalyst
JPH10165817A (en) Exhaust gas purification catalyst
JPH07132226A (en) Exhaust gas purification catalyst
JPH07171392A (en) Exhaust gas purification catalyst
JP3551346B2 (en) Exhaust gas purification equipment
JP3764760B2 (en) Catalyst for purifying exhaust gas from lean burn engine and purification method
JPH08281071A (en) Exhaust gas purification method and exhaust gas purification catalyst
JPH0523593A (en) Exhaust emission control system
JPH0857315A (en) Exhaust gas purification catalyst
JP3338889B2 (en) Exhaust gas purification device
JP3826476B2 (en) Exhaust gas purification catalyst and method for producing the same

Legal Events

Date Code Title Description
FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20070906

Year of fee payment: 5

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20080906

Year of fee payment: 6

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20080906

Year of fee payment: 6

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20090906

Year of fee payment: 7

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20100906

Year of fee payment: 8

LAPS Cancellation because of no payment of annual fees